FIELD OF THE INVENTION
[0001] This invention relates to a method of and an apparatus for extracting chemicals from
a solution and, more particularly, to extracting chemical species, for,
inter alia, general chemical analysis.
BACKGROUND TO THE INVENTION
[0002] The extraction and consequent concentration of chemical species from a variety of
aqueous solutions is of great importance for a number of disciplines. A medical practitioner
must be in a position to diagnose an ailment precisely and needs accurate indications
of a range of vascular or cellular chemical compositions. Similarly, precise determinations
of the concentration of a range of chemicals are necessary for a scientist working
in, for example, the environmental field before the state of health or pollution of
a wetlands ecosystem can be ascertained.
[0003] The above represent only two types of situation where the extraction or separation
of specific chemical compositions from a solution is important.
[0004] With regard to the historical development of separation or extraction techniques,
at first it was directed at developing techniques that are capable of extracting as
many compounds as possible with minimal organic solvents for multi-residue analysis
[1]. Later, the focus shifted more to techniques that are capable of fast response
times and high sample throughput such as immunoassays [2]. More recently, attention
has been concentrated on simple and miniaturised techniques, capable of easy coupling
to analytical instruments. Such novel, simple and miniaturised extraction techniques
that have been accepted by the scientific community in analytical sciences include
Solid-Phase Micro-Extraction (SPME) [3] and Stir-Bar Sorptive Extraction (SBSE) techniques
[4]. However, these novel techniques mainly use extraction sorbents that interact
with the analytes through hydrophobic interactions, and this makes them unsuitable
for applications that involve complex matrices samples such as wastewater, plant extracts
and biological fluids. SPME is also mainly suitable for analytes with a very high
octanol-water partition coefficient (K
o/w > 20 000 for a 10-mL sample) due to the small volume of poly(dimethylsiloxane)-coating
(PDMS-coating) used [5].
[0006] It should be noted that in this specification and in the claims the term "desired
chemical composition" or "desired chemical" is intended to refer to a chemical composition
which is extracted from a solution containing the same.
OBJECT OF THE INVENTION
[0007] It is an object of this invention to provide a method for extracting chemicals from
a solution and, more particularly, for extracting chemical species, for,
inter alia, general chemical analysis.
SUMMARY OF THE INVENTION
[0008] In accordance with this invention there is provided a method for extracting at least
one desired chemical composition from a solution comprising placing a solution containing
the desired chemical composition into a first chamber, placing an adsorbent material
which, in use, selectively adsorbs and forms a complex with the desired chemical composition
into a second chamber which is in fluid communication with the first chamber but separated
therefrom by a liquid membrane which allows passage therethrough of the desired chemical
composition to be extracted but impedes the passage of the desired chemical composition
and adsorbent complex, allowing the desired chemical composition to diffuse across
the membrane to be adsorbed by and form a complex with the adsorbent material, and
removing the adsorbent material and desired chemical composition complex from the
second chamber.
[0009] There is also provided for the first and second chambers to be contained within a
single vessel and for the second chamber to be formed from a bag fashioned from the
liquid membrane. Alternatively there is provided for the membrane to be fashioned
into a number, preferably a plurality and further preferably a multiplicity, of hollow
fibres, the inside or insides of which contain the adsorbent material and form the
second chamber.
[0010] There is further provided for the adsorbent material to be in a solution, preferably
a solution including an organic solvent, further preferably toluene. Alternatively
there is provided for the adsorbent material to be an antibody. Further alternatively
for the adsorbent material to be an antibody, for the adsorbent material to be a polymer,
preferably a molecularly imprinted polymer, in the form of beads, alternatively fibres.
[0011] There is further provided for the solution containing the desired chemical composition
to be an aqueous solution.
[0012] There is further provided for the second chamber to contain a number of different
adsorbent materials each of which, in use, selectively adsorbs and, consequently extracts,
a different chemical composition from the solution in the first chamber.
[0013] According to a further aspect, there is provided an analytical method for analyzing
at least one chemical composition comprising adsorbing the chemical composition onto
an adsorbent material which selectively adsorbs and forms a complex with the desired
chemical composition is placed as described above and, subsequently, performing a
desired analysed on the adsorbed chemical composition using techniques well known
in the art.
BRIEF DESCRIPTION OF THE FIGURES
[0014] The above and additional aspects of the invention will be described below by way
of example only and with reference to the accompanying figures in which:
- Figure 1
- A laboratory scale set-up of the polymerisation process in an oil bath at 60°C.
- Figure 2:
- Set-up of the LM-MIP extraction technique.
- Figure 3:
- Scanning electron microscope pictures of polymer beads.
- Figure 4:
- Plot of obtained extraction efficiency against the amount of MIP in the organic acceptor
solution
- Figure 5:
- Plot of obtained extraction efficiency against different organic solvents in the acceptor
phase
- Figure 6:
- Plot of obtained extraction efficiency against different desorption solvents of the
triazines from the MIP beads
- Figure 7:
- Plot of obtained extraction efficiency against the different extraction times. Figure
8: Chromatograms obtained after direct injection of vegetable extract
- Figure 9:
- Chromatograms obtained after direct injection of apple extract spiked
DETAILED DESCRIPTION OF ONE EMBODIMENT
[0015] In a non-limiting embodiment of the invention which was aimed at testing for the
extraction of triazine herbicides in fruit samples, a combination of Liquid Membranes
(LM's) and Molecularly Imprinted Polymers (MIP's) is used. The embodiment takes advantage
of both technologies for preparing what is envisaged to be an efficient extraction
technique (LM-MIP extraction technique) but, the above notwithstanding, it must be
appreciated that any material, including polymers and antibodies, which can adsorb
selectively a desired chemical composition or species may be used.
[0016] Triazine herbicides are widely used as herbicides in many countries and therefore
of environmental concern [6].
Scientific and technological background to Molecularly Imprinted Polymers (MIP's).
[0017] MIP's are made by synthesising cross-linked polymers in the presence of a template
molecule (analyte). After removal of the template molecule from a resulting polymer
network, specific recognition sites, that are complementary to the template in terms
of their size, shape and functionality, are left. These materials are being extensively
investigated for use as highly selective sorbents for clean-up and preconcentration
of samples prior to analysis [7-10].
[0018] Another advantage of MIP's is that they are highly robust and can tolerate harsh
conditions such as extreme pH, high temperature and pressure. However, for special
environmental and biomedical applications, the technology still faces some challenges.
For example, the binding site population may show heterogeneity, the mass transfer
can in some instances be low, the template leakage may be of concern at limiting concentrations,
and the performance is best in organic solvents that are often used in the preparation.
Many of these challenges have nevertheless been successfully met by, for example,
the use of semicovalent methods to increase binding site homogeneity, and the use
of structural template analogues to avoid leakage [11].
[0019] MIP's have also been used for selective elution instead of selective extraction so
that aqueous samples can be percolated [12]. Investigations on using aqueous buffer
sample solutions instead of only water sample has also been reported in trying to
extract samples directly onto MIP sorbents [13]. However, a remaining major challenge
is to design and prepare MIP's to perform well in aqueous media. Several approaches
have been used to address this problem, including the direct use of metal coordination-based
recognition, but it has proven difficult to present a general solution to the situation.
This is limiting current MIP-applications of the extraction of complex aqueous sample
solutions. In a previous study, C
18-silica-columns were coupled with MIP-columns connected online to liquid chromatography
[14]. This has allowed the percolation of aqueous water samples first onto a C
18-silica-sorbent and eluting it with organic solvent onto a MIP-column. This approach
proved successful but required a rather complicated set-up including a number of valves
and pumps for controlling the solutions flow system.
[0020] Membrane technology is currently identified as a very powerful approach in analytical
sciences in that it offers various versions of simple, miniaturised and novel extraction
configurations/techniques [15-17]. The general principle of membrane extraction is
that one has two compartments, a donor and an acceptor phases separated by nonporous
membrane or porous membrane impregnated with an organic solvent [18]. Target compounds
diffuse from the donor solution through the membrane into the acceptor phase. Various
compositions of the donor and acceptor phases have been reported to enhance the selectivity,
such as adjusting the pH of the donor and acceptor phases such that only uncharged
organic compounds dissolve into the membrane and are ionized once in the acceptor
phase [18]. However, despite these adjustments, selectivity obtained in membrane extraction
techniques is not enough when extracting complex samples such as wastewater, plant
and vegetable extracts etc.
[0021] In accordance with the present invention the approach was to combine Liquid Membrane
(LM) extraction and Molecularly Imprinted Polymer (MIP) to get what is referred to
as LM-MIP extraction technique. Such a technique addresses the short comings of both
LM and MIP to give very selective extraction.
[0022] The developed extraction technique carries both academic and industrial significance
as it addresses central challenges in present MIP- and LM-technologies. The combination
of the two techniques into a working unit has the potential to create synergy effects
that may meet these challenges both in terms of aqueous phase performance and analyte
selectivity. The LM-MIP-technique is also highly adaptable to versatile and miniaturised
production formats, and has the potential to be commercialised.
Configuration of the LM-MIP extraction technique
[0023] The configuration of the LM-MIP extraction technique is shown in Figure 1.
[0024] It consists of a container that could be made out of inert material such as glass
or poly tetra flouro ethylene (PTFE). The container contains two compartments separated
by a liquid membrane or nonporous hydrophobic membrane such as silicone rubber. One
compartment is the donor containing the sample say in aqueous solution while the other
is the acceptor phase filled with an organic liquid. In a case where a liquid membrane
is used, organic liquid filling the acceptor phase is also the liquid membrane. The
acceptor solution then contains MIP beads or MIP fibre. These are synthesized from
the compound that is extracted from the water samples. Another configuration is where
a hollow fibre is used. The hollow fibre separates two compartments, the donor containing
the sample say in aqueous solution while the inside of the hollow fibre serves as
the other compartment filled with an organic liquid. The organic liquid contains MIP
beads or MIP fibre.
Specific objectives and expected significance of the current embodiment
[0025]
a. To combine the technologies of Molecularly Imprinted Polymers (MIP's) and Liquid
Membranes (LM's), offering unsurpassed selectivity in environmental and biomedical
applications;
b. to develop new extraction technique based on the combined MIP-LM-technology;
c. to further develop the extraction technique into a miniaturised format, still retaining
its simplicity; and
d. to apply the developed extraction for extraction and preconcentration of various
organic compounds in various complicated samples such as wastewater.
EXPERIMENTAL
Chemicals
[0026] S'imazine, atrazine, propazine, 2,2'-Azobis(2-isobutyronitrile) (AIBN), methacrylic
acid (MAA), trimethylolpropane trimethacrylate (TRIM) and 1,1 Azobis(cyclohexane-carbonitrile)
(ACCN) were purchased from Sigma Aldrich (Darmstadt, Germany). Organic solvents were
from BDH, (London, England). All solvents used were of analytical grade. Silicone
oil was bought from Kynethan Business Management (KBM) (Johannesburg, South Africa).
The oil was added as a bath to heat the reaction mixture in the synthesis of molecular
imprinting polymer for Triazine compounds.
Apparatus
[0027] HPLC used in this project was from SRI (model 210D, LA, California, USA). It consisted
of variable UV detector from which 220 nm was selected for detection of triazines.
A C
18 column (5 µm x 4.6 mm x 25 cm) was from Supelco (Darmstadt, Germany). A computer
equipped with peak simple chromatographic software (version 3.29) was used to process
chromatograms.
[0028] An MSE, Mistral 1000 bench top centrifuge (Hettich, Germany) was used to sediment
the MIPs during washing after synthesis and for shaking or dissolving sample solutions,
a 460 Ultrasonic Elma (Braun, Germany) was used. The physical appearance of MIPs was
viewed using scanning electron microscopes JSM-840 (JEOL, JMS-840, and Tokyo, Japan).
[0029] Porous PTFE membrane with polyethylene backing (pore size 0.2 µm, porosity 0.70 µm,
total thickness 175 µm of which 115 µm is polyethylene backing, Type FG) was from
Millipore (Bedford, MA, USA). The stainless steel extraction unit was constructed
by CE engineering cc (Johannesburg, South Africa).
Types of samples
[0030] To demonstrate the potential of the extraction technique to food samples, apple fruit
and lettuce vegetable were investigated. Both food samples were bought from a local
food shop and were picked randomly.
Preparation of imprinted polymers
[0031] The MIP preparation method was done as follows;1 mmol of atrazine, 8 mmol of monomer
(MAA), 25 mmol of cross-linking agent ethylene glycol dimethacrylate (EDMA) and 50
mg of initiator 2,2-azobis(2,4-dimethylvaleronitrile) (ABDV) were dissolved in 7.5
ml of acetonitrile in an air-tight glass vial. The mixture was then purged with nitrogen
for 5 min. The polymerisation was done overnight at 60 °C in an oil-bath. The bulk
polymers were successively ground in a mortar and crushed with ceramic beads in presence
of methanol and washed with acetonitrile / acetic acid mixture (4:1v/v 5 x 10 ml)
followed by acetonitrile (1 x 10 ml) and methanol (2 x 10 ml) at 60°C with shaking.
The polymers were then dried overnight with a vacuum pump. Particle sizes in the range
25-90 µm were taken using two stainless steel sieves. The experimental apparatus in
which the MIP was prepared is shown in Figure 1.
Sample preparation
[0032] Both food samples were crushed and homogenised and 4 grams of vegetable and 40 grams
of the apple were taken. To each of these, 150 ml of methanol was added. The samples
were then sonicated for 30 minutes and left to stand for an hour. Then it was filtered
through 0.45 µm filter paper. The filtrate was left to evaporate overnight. 150 ml
of phosphate buffer at pH 7 was added to the thick liquid that remained. This was
filtered once more and the filtrate was spiked with appropriate amount of Triazines
and then extracted. Blanks samples were treated in the same way.
Preparing 0.2M phosphate buffer
[0033] The phosphate buffer at pH 7 was prepared by dissolving 20.75g Na
2HPO
4 and 5.03g NaH
2PO
4 in 500 ml deionised water.
Analysis
Standard solutions
[0034] 50 mg of each triazine was dissolved in 50 ml volumetric flask of methanol to make
a stock solution of 1000 mg L
-1. All the standards with the concentration of 0.25, 0.5, 1, 1.5, 2, and 2.5 mg L
-1 were prepared from the stock solution. The prepared mobile phase was filtered twice
and sonicated for 20 minutes in order to get rid of air bubbles.
HPLC
[0035] HPLC used in this project was from SRI (model 210D, LA, California, USA). It consisted
of variable UV detector from which 220 nm was selected for detection of triazines.
A C
18 column (5 µm x 4.6 mm x 25 cm) was from Supelco (Darmstadt, Germany). A computer
equipped with peak simple chromatographic software (version 3.29) was used to process
chromatograms. HPLC mobile phase was composed of 60% acetonitrile and 40% deionised
water.
Preparing mobile phase
[0036] The prepared mobile phase was filtered twice and sonicated for 20 minutes. This was
done to eliminate any particles and above all to remove dissolved air that would form
bubbles when eluting.
Reproducibility studies
[0037] The reproducibility study was done by injecting a standard solution 10 times. The
results obtained gave standard deviation of 2.22 and % RSD of 13.2.
Sample extraction
Liquid-membrane -molecular imprinted polymer (LM-MIP) extraction
[0038] Preparation of the extraction unit involved first filling 37 ml of the sample in
the lower compartment (Figure 2). The membrane previously soaked for 5 minutes in
organic liquid usually, toluene was placed on top. The upper compartment was then
screwed. 2.5 ml of the organic liquid followed by 10 mg of MIP beads were then added.
The top hole was then closed and the unit was ready for extraction after shaking the
unit to disperse the added MIP beads. Triazine compounds were extracted from aqueous
phase into organic acceptor phase due to their solubility where they were bound onto
MIP beads. After 90 minutes extraction, MIP beads were separated from the organic
phase by passing the whole content through a 0.1 µm syringe filter. The MIP beads
were retained. Non specific bound compounds were washed off the MIP by passing through
2 ml of dichloromethane. Using a small syringe, 3 ml of methanol in water (90:10%)
was passed through to release the bound triazines which was then analysed on HPLC.
[0039] In some experiments, MMLLE was performed without the MIP in the acceptor phase so
as to compare the selectivity to the combination. For this purpose, after MMLLE, the
acceptor solution was taken out and left to evaporate at room temperature. Then 0.5
ml of hexane-ethyl acetate (3:2) was added and injected into the HPLC.
RESULTS AND DISCUSSIONS
Synthesis of MIPs
[0040] MIP preparation for triazine compounds is given in the experimental. The percentage
yield was 100 %. Bulk polymers are much larger than those of precipitation polymerisation.
The used bulk polymers were about 20-90 µm. These sizes were important because after
extraction, the whole acceptor phase was passed through a 0.2 µm filter where the
MIP beads were trapped allowing only the organic solvent to pass through. A picture
of scanning electron microscope of molecularly imprinted polymers prepared by bulk
polymerisation where dry polymer was placed on aluminium and plated with carbon and
gold/platinum mixture is shown in Figure 3. The image was taken using JSP at 2000x
magnification.
Impurities in the prepared MIPs
[0041] Complete template extraction from the prepared MIP is a crucial step as this leaves
selective cavities ready for analyte recognition and prevents breeding during application.
In our study, Soxhlet extraction was used and the last washing solution was injected
directly and also preconcentrated first before injection into the HPLC to test for
impurities. No Triazine peak was detected. This suggests that most of the template
was removed from the polymer.
Variation of the amount of MIPs in the acceptor phase
[0042] Several factors govern the binding capacity of MIP beads. These factors include surface
area, the pore size, pore size distribution and amount of MIP. Smaller particles are
expected to have high surface area compared to bigger particles. Increase in amount
of MIP beads lead to an increase in the triazine bound (Figure 4) as expected. The
triazines re-binding were a little faster for propazine and atrazine compared to simazine
(Figure 4). These differences are related to the structure of the compounds. The MIP
was prepared with atrazine as template so it is expected to be bound more efficiently
compared to others. However, the structure of propazine is much closer to atrazine
so the two should have close rebinding kinetics.
[0043] A plot of obtained extraction efficiency against the amount of MIP in the organic
acceptor solution (hexane-ethyl acetate; 3:2) is shown in Figure 4. Extraction time
was for 60 minutes and 1 mg L
-1 of triazine mixture spiked in deionised water as sample. Fresh acceptor solution
(2 ml) was used as a washing solution of MIP followed by 3 ml of methanol as desorption
solvent.
Influence of the organic acceptor solution on the re-binding of Triazine compounds
onto MIP beads.
[0044] In this set-up, the best solvent is the one that gives high partitioning of the triazines
from the aqueous phase and also allows the triazine re-binding onto MIP beads without
any hindrance or competition. Several solvents were thus screened as possible acceptor
solution. The results shown in Figure 5 indicate that more triazines were extracted
with toluene as solvent which was used as porogen in MIP preparation. Factors that
govern analyte-solvent interaction are van der Waals forces that include hydrogen
bonding, dipole-dipole and london dispersion. Solvents with less of these forces would
thus be preferred for triazine re-binding onto MIP beads. However, some of these forces
are needed to have high partitioning of triazines from the aqueous phase into the
organic solvent. Acetonitrile gave the least amount extracted. This could due to the
fact that it could not make a stable liquid membrane. A plot of obtained extraction
efficiency against different organic solvents in the acceptor phase is shown in Figure
5. Extraction time was for 60 minutes and 1 mg L
-1 of triazine mixture spiked in deionised water was extracted with 7 mg of MIP in the
organic acceptor solution. 2 ml of hexane-ethyl acetate (3:2) was used as a washing
solution of MIP followed by 3 ml of methanol as desorption solvent.
Washing solvent
[0045] The best washing solvent should take the entire interfering matrix bound by nonspecific
binding leaving target compounds still bound. Washing solvents such as toluene, hexane
and dichloromethane were tested. Dichloromethane was chosen as the best solvent as
it gave much cleaner chromatograms and high enrichments after analyte desorption from
the MIP beads. Solvents such as ethyl acetate, acetonitrile, butyl methyl ketone,
toluene and dichloromethane were screened but not detail. Since the polymer was prepared
in toluene, it was supposed to give the best washing. However, dichloromethane which
has the lowest hydrogen bond parameter among other solvents studied was chosen as
the best choice.
Influence of the amount of desorption solvent
[0046] The best solvent is one that elutes the trapped analytes preferably at one goal and
with minimal volume to avoid dilution of the analytes. Figure 6 shows the results
on the studying the type of desorption solvent from MIP binds. 90% methanol in water
was found to be the best solvent compared to methanol, water and acetonitrile. A good
solvent should be able to disrupt the interaction between the polymer and trapped
analytes which is mainly hydrogen bonding. A plot of obtained extraction efficiency
against different desorption solvents of the triazines from MIP beads is shown in
Figure 6.
Varying extraction time
[0047] Figure 7 shows the results of varying the extraction time. The amount of triazines
extracted increased with extraction time. This is expected since both diffusion of
triazines from the donor side of the extraction unit through the membrane into the
bulk acceptor phase and subsequent re-binding is time dependant. More time allows
triazines to diffuse through the membrane leading to more re-binding onto MIP beads.
However, at around 90 minutes, there are signs of reaching a plateau especially for
atrazine and propazine. 90 minutes was thus taken as optimum extraction time since
it was a compromise between high extraction and sample throughput.
MMLLE-MIP technique extraction of food samples.
[0048] The selectivity of the MMLLE-MIP technique was demonstrated by extraction spiked
vegetable and fruit extracts. The obtained chromatograms are given in Figures 8 and
9. In Figure 8a, a direct injection of the vegetable extract spiked with 100 µg L
-1 gave very small triazine peaks and huge peak due to matrix effects. Injection of
the organic acceptor solution after MMLLE extraction of 30 µg L
-1 of the triazine mixture spiked in a vegetable extract only did not improve the chromatogram
(Figure 8b). A combination of MMLLE-MIP (Figure 8c) gave clean and much bigger peaks.
The same observations can be seen in an apple extract (Figure 9).
[0049] Table 1 shows a comparison of extraction efficiency and enrichment factors for the
Triazine compounds obtained in vegetable and apple extracts. The results show that
the extraction process is independent of sample matrix. This is expected since the
MMLLE-MIP technique is very selective.
Table 1: Comparison of extraction efficiency (E
A) and enrichment factor (E
n) after extraction of 0.03 mg L
-1 of triazine mixture spiked in lettuce and apple extracts. The experiments were performed
at optimized conditions (see figure 8). Values in brackets are percentage relative
standard deviations.
| Compound |
Lettuce vegetable extract |
Apple fruit extract |
| |
EA |
En |
EA |
En |
| Simazine |
53 (7) |
40 |
55 (5) |
42 |
| Atrazine |
60 (10) |
43 |
63 (15) |
45 |
| Propazine |
55 (8) |
42 |
60 (4) |
43 |
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1. A method for extracting at least one desired chemical composition from a solution
comprising placing a solution containing the desired chemical composition into a first
chamber, placing an adsorbent material which, in use, selectively adsorbs and forms
a complex with the desired chemical composition into a second chamber which is in
fluid communication with the first chamber but separated therefrom by a liquid membrane
which allows passage therethrough of the desired chemical composition to be extracted
but impedes the passage of the desired chemical composition and adsorbent complex,
allowing the desired chemical composition to diffuse across the membrane to be adsorbed
by and form a complex with the adsorbent material, and removing the adsorbent material
and desired chemical composition complex from the second chamber characterised in that the first and second chambers are contained within a single vessel.
2. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 1 characterised in that the second chamber is formed from a bag fashioned from the liquid membrane.
3. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 1 or in claim 2 characterised in that the membrane is fashioned into a number of hollow fibres, the inside or insides of
which contain the adsorbent material and form the second chamber.
4. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 3 characterised in that the membrane is fashioned into a plurality of hollow fibres.
5. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 3 characterised in that the membrane is fashioned into a multiplicity of hollow fibres.
6. A method for extracting at least one desired chemical composition from a solution
as claimed in any one of the preceding claims characterised in that the adsorbent material is in a solution.
7. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 6 characterised in that the solution includes an organic solvent.
8. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 7 characterised in that the organic solvent is toluene.
9. A method for extracting at least one desired chemical composition from a solution
as claimed in any one of the claims 1 to 6 characterised in that the adsorbent material is an antibody.
10. A method for extracting at least one desired chemical composition from a solution
as claimed in any one of the claims 1 to 6 characterised in that the adsorbent material is a polymer.
11. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 10 characterised in that the polymer is a molecularly imprinted polymer.
12. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 11 characterised in that the polymer is in the form of beads.
13. A method for extracting at least one desired chemical composition from a solution
as claimed in claim 11 characterised in that the polymer is in the form of fibres.
14. A method for extracting at least one desired chemical composition from a solution
as claimed in any one of the preceding claims characterised in that the solution containing the desired chemical composition is an aqueous solution.
15. A method for extracting at least one desired chemical composition from a solution
as claimed in any one of the preceding claims characterised in that the second chamber contains a number of different adsorbent materials each of which,
in use, selectively adsorbs and, consequently extracts, a different chemical composition
from the solution in the first chamber.
1. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung umfassend
Einstellen einer Lösung, die die gewünschte chemische Zusammensetzung enthält, in
eine erste Kammer,
Einstellen eines Adsorbermaterials, das bei Gebrauch selektiv adsorbiert und einen
Komplex mit der gewünschten chemischen Zusammensetzung bildet in eine zweite Kammer,
die im Flüssigkeitsaustausch mit der ersten Kammer steht, aber von dieser durch eine
Flüssigkeitsmembran getrennt ist, die den Durchfluss der gewünschten chemischen Zusammensetzung,
die extrahiert werden soll, durch diese erlaubt, aber den Durchfluss der gewünschten
chemischen Zusammensetzung und des Adsorberkomplexes verhindert, sodass die gewünschte
chemische Zusammensetzung durch die Membran diffundiert, und vom Adsorbermaterial
adsorbiert wird und einen Komplex mit dem Adsorbermaterial bildet,
und Entfernen des Adsorbermaterials und des gewünschten chemischen Zusammensetzungskomplexes
aus der zweiten Kammer, dadurch gekennzeichnet, dass die erste und die zweite Kammer sich in einem einzigen Behälter befinden.
2. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 1, dadurch gekennzeichnet, dass die zweite Kammer aus einem Beutel gebildet wird, der aus einer Flüssigkeitsmembran
hergestellt wird.
3. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 1 oder Anspruch 2, dadurch gekennzeichnet, dass die Membran in einer Anzahl von Hohlfasern gestaltet wird, deren Innenseite oder
deren Innenseiten das Adsorbermaterial enthalten und die zweite Kammer bilden.
4. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 3, dadurch gekennzeichnet, dass die Membran in einer Mehrzahl von Hohlfasern gestaltet wird.
5. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 3, dadurch gekennzeichnet, dass die Membran in einer Vielzahl von Hohlfasern gestaltet wird.
6. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß einem der vorhergehenden Ansprüche, dadurch gekennzeichnet, dass das Adsorbermaterial in einer Lösung vorliegt.
7. Ein Verfahren zum Extrahieren von wenigstens einer chemischen Zusammensetzung aus
einer Lösung gemäß Anspruch 6, dadurch gekennzeichnet, dass die Lösung ein organisches Lösungsmittel umfasst.
8. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 7, dadurch gekennzeichnet, dass das organische Lösungsmittel Toluol ist.
9. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß einem oder mehreren der Ansprüche 1 bis 6, dadurch gekennzeichnet, dass das Adsorbermaterial ein Antikörper ist.
10. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß einem oder mehreren der Ansprüche 1 bis 6, dadurch gekennzeichnet, dass das Adsorbermaterial ein Polymer ist.
11. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 10, dadurch gekennzeichnet, dass das Polymer ein molekular geprägtes Polymer ist.
12. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 11, dadurch gekennzeichnet, dass das Polymer in der Form von Kügelchen vorliegt.
13. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß Anspruch 11, dadurch gekennzeichnet, dass das Polymer in der Form von Fasern vorliegt.
14. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß einem oder mehreren der vorhergehenden Ansprüche, dadurch gekennzeichnet, dass die Lösung, die die gewünschte chemische Zusammensetzung enthält, eine wässrige Lösung
ist.
15. Ein Verfahren zum Extrahieren von wenigstens einer gewünschten chemischen Zusammensetzung
aus einer Lösung gemäß einem oder mehreren der vorhergehenden Ansprüche, dadurch gekennzeichnet, dass die zweite Kammer eine Reihe von verschiedenen Adsorbermaterialien enthält, von denen
jedes bei Gebrauch selektiv adsorbiert und folglich eine verschiedene chemische Zusammensetzung
aus der Lösung in der ersten Kammer extrahiert.
1. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution, qui comprend : le placement d'une solution contenant la composition chimique
souhaitée dans une première chambre ; le placement d'un matériau adsorbant qui, en
service, adsorbe de manière sélective et forme un complexe avec la composition chimique
souhaitée, dans une seconde chambre qui est en communication de fluide avec la première
chambre mais qui est séparée de celle-ci par une membrane liquide qui permet un passage
à travers celle-ci de la composition chimique souhaitée à extraire mais empêche le
passage du complexe de matériau adsorbant et de composition chimique souhaitée, en
permettant à la composition chimique souhaitée de diffuser à travers la membrane pour
être adsorbée par, et former un complexe avec, le matériau adsorbant ; et l'élimination
du complexe de matériau adsorbant et de composition chimique souhaitée de la seconde
chambre, caractérisé en ce que les première et seconde chambres sont contenues à l'intérieur d'un seul contenant.
2. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 1, caractérisé en ce que la seconde chambre est formée à partir d'un sac façonné à partir de la membrane liquide.
3. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 1 ou 2, caractérisé en ce que la membrane est façonnée dans un certain nombre de fibres creuses, dont le ou les
intérieurs contiennent le matériau adsorbant et forment la seconde chambre.
4. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 3, caractérisé en ce que la membrane est façonnée dans une pluralité de fibres creuses.
5. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 3, caractérisé en ce que la membrane est façonnée dans une multiplicité de fibres creuses.
6. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon l'une quelconque des revendications précédentes, caractérisé en ce que le matériau adsorbant se trouve dans une solution.
7. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 6, caractérisé en ce que la solution comprend un solvant organique.
8. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 7, caractérisé en ce que le solvant organique est du toluène.
9. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon l'une quelconque des revendications 1 à 6, caractérisé en ce que le matériau adsorbant est un anticorps.
10. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon l'une quelconque des revendications 1 à 6, caractérisé en ce que le matériau adsorbant est un polymère.
11. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 10, caractérisé en ce que le polymère est un polymère à empreinte moléculaire.
12. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 11, caractérisé en ce que le polymère se présente sous la forme de perles.
13. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon la revendication 11, caractérisé en ce que le polymère se présente sous la forme de fibres.
14. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon l'une quelconque des revendications précédentes, caractérisé en ce que la solution contenant la composition chimique souhaitée est une solution aqueuse.
15. Procédé destiné à extraire au moins une composition chimique souhaitée à partir d'une
solution selon l'une quelconque des revendications précédentes, caractérisé en ce que la seconde chambre contient un certain nombre de différents matériaux adsorbants,
chacun d'eux, en service, adsorbant de manière sélective et, par conséquent extrayant,
une composition chimique différente à partir de la solution présente dans la première
chambre.